IEER SDA Vol. 5 No. 3

Health and Environmental Impacts
of Nuclear Weapons Production

Assessments of the harm done by nuclear weapons plants to both workers and neighbors have generally relied on the radiation data provided by the Department of Energy (DOE) and its contractors. Detailed studies of the DOE's uranium processing plant near Fernald, Ohio, (commonly called the Fernald plant), show that DOE and contractor assessments are fundamentally flawed in numerous ways and that harm to both neighbors and workers was far greater than the DOE acknowledged. Further, preliminary indications are that the conditions that gave rise to the DOE's false reassurances of safety and environmental compliance are also likely to be present at a number of other nuclear weapons plants.

This issue of the newsletter has three articles on health and environmental impacts of nuclear weapons production: i) a general overview of how health and dose reconstruction studies are done; ii) a case study of the Fernald plant regarding radiation exposure and health risk to its neighbors; and iii) a case study of worker exposure at the Fernald plant

We will continue this series in future newsletters. Note that these evaluations only address exposures for the period when nuclear weapons plants were operating. They do not include risks posed by the wastes that have been created since, or from decontamination and decommissioning operations that are needed at all weapons plants and test sites.


Radioactivity in the Fernald Neighborhood

By: Arjun Makhijani

The Department of Energy's Feed Materials Production Center (also called the Fernald plant), located near Fernald, Ohio, produced uranium metal mainly for use in plutonium production at the Savannah River Site in South Carolina and at Hanford in Washington state. The plant was operated by National Lead of Ohio (NLO) from 1951 through 1985. In 1986 it was taken over by Westinghouse. NLO had a number of subcontractors, (the Alba Craft plant in Oxford, Ohio, for example), who performed a variety of tasks such as machining of uranium metal. The Fernald plant closed in 1989, and the site now has a new name: the Fernald Environmental Restoration Management Corporation (FERMCO). It is currently being remediated by the DOE contractor, Fluor Daniel.

The Fernald plant consisted of 10 production operations (called "plants") as well as other support buildings. In these facilities, uranium in various forms, including ore concentrates, scrap, and recycled material containing uranium were processed to produce uranium metal. The six waste pits at the site contain both radioactive and non-radioactive chemicals, including uranium isotopes, thorium-230 (a waste material from the uranium production process), thorium-232, and barium salts. In addition, the K-65 silos located on the site contain radium-226, a decay product of uranium which emits radon (see centerfold). Figure 1 shows a schematic diagram of uranium processing operations at Fernald.


Source: Voilleque et al., Fernald Dosimetry Reconstruction Project, Tasks 2 and 3: Radionuclide Source Terms and Uncertainties (Neeses, SC: Radiological Assessments Corporation, 1995), p. B-2.

Throughout the history of the plant's operation the DOE and its contractors consistently asserted that the offsite residents were not harmed by its operation and that exposures were within allowable limits. These assertions were challenged in a 1985 class-action lawsuit brought against NLO by neighbors of the plant. In that year, Lisa Crawford, the lead plaintiff, had discovered that the well that she and her family had been using for drinking water was contaminated with uranium. She also found out that the DOE and NLO had discovered the contamination four years earlier but had not informed her. Ms. Crawford realized her well was contaminated after she requested monitoring data in the aftermath of a highly publicized accidental uranium release from the plant in late 1984.

The Fernald plant had, in fact, released a number of radioactive and non-radioactive pollutants to the air and water, but DOE had very partial data for some of these materials, and none at all for many others. Among the pollutants were: uranium, thorium, radon gas, radium, technetium-99, ammonia, hydrofluoric acid, fluorine, nitric acid, kerosene, chromium, and lead. The most important radioactive pollution consisted of releases of uranium and radon gas to the air. Detailed evaluations of non-radioactive pollutant releases have not yet been done and few data exist on which such evaluations can be based.

Uranium releases

Internal evaluations of the plant's operations were initiated in 1985 and they continued until the plant was shut down in 1989. In early 1985, NLO estimated that the releases of uranium over the 34-year period from 1951, when parts of the plant were started up, to 1984 were about 200,000 pounds. The NLO estimate was increased to 300,000 pounds by 1987 after inclusion of estimates of some of the most serious emissions during the 1950s. There were a number of evident deficiencies in these official estimates. Among the more egregious errors were:1

  • An assumption that releases were zero when there were no data.
  • An assumption that scrubbers designed to remove uranium from highly acidic exhaust always operated within manufacturer specified efficiency, despite internal plant data to the contrary.
  • The use of an incorrect formula to calculate scrubber releases under conditions of variable efficiency.
  • Inclusion of fabricated data that showed that releases were zero at locations and times when no measurements were being made.
  • A failure to account for poor dust collector efficiency and frequent problems with dust collector equipment.
  • Poor industrial hygiene practices, such as leaving radioactive materials to dry in trays in doorways, and operating equipment that was in poor condition.

IEER was retained in 1987 by the law firm of Waite, Schneider, Bayless, and Chesley to do some of the expert studies for the class action lawsuit. IEER's review of the historical documents showed that plant officials were aware of many of these deficiencies. For instance, the use of the incorrect formula for scrubber releases was pointed out in a 1971 memo by a plant engineer, who called it "inherently deceptive" because it resulted in release estimates that grew smaller as the scrubber efficiency deteriorated -- the opposite of the truth. Figure 2 shows the actual releases of uranium compared to the NLO estimates for an example in which uranium in the air going into the scrubber was 100 kilograms.

FIGURE 2: Variation of Efficiency of Airborne Uranium Releases from FMPC Scrubbers for an Assumed Inlet Uranium Loading of 100 Kg*

Source: Makhijani and Franke, 1989
* This is the amount of uranium in the gas going into the scrubber.

A 1955 document pointed to early problems with uranium release estimates: "We realize in most instances that these estimates [for stack losses from plants 4 and 7] are far below your true stack losses."2 Plant 7 was shut down in 1956 due to operational problems. Plant 4 continued to operate until Fernald shut down, and the problem of corrosion of dust collector equipment by acidic exhaust continued for decades.

The following example also illustrates the poor industrial hygiene practices at the plant:

Probably the worst housekeeping problem in the facility is the Ball Mill. The equipment leaks excessively at practically every joint. All horizontal surfaces have a thick covering of dust....Since the ventilation is inadequate and these is no proper enclosure, a bucket was placed under the largest leak to help contain the spilled dust.3

Such discharges of radioactive materials were not measured and were disregarded in the official release estimates and public reassurances.

Under the glare of public scrutiny and the class-action lawsuit, Westinghouse, the new contractor (and not named as a defendant), revised the official figures for the 1951-1985 period again and stated that the releases were in the range of 395,000 to 552,000 pounds. While these estimates were higher, they still disregarded many known facts. For instance, unmeasured losses over the plant's entire 37-year history were estimated at about 700 pounds, while an internal plant document stated that unmeasured losses were more than that in a single month.

During work on the lawsuit in 1988 and 1989, IEER focused its work on estimating uranium losses, since that was the main material processed and data on other materials released to the air were scarce or non-existent. We re-estimated losses from several important sources, notably scrubbers in the scrap recovery plant (Plant 8). We also made an estimate of uranium releases based on measurements of uranium in the soil around the plant. Our work was admittedly very preliminary, mainly since IEER was unable to obtain most of the crucial documents regarding plant operation and pollution control equipment efficiencies. Moreover, the quality of the data that we had was poor and some of it was internally inconsistent.

Still, we concluded that the official estimates were almost certainly wrong, that the releases were higher than the upper end of the official estimate of 552,000 pounds, and that uranium air concentration standards had been violated on at least some occasions. IEER estimated that uranium releases were in the range of 600,000 to 3 million pounds, with a middle estimate of 900,000 pounds. IEER also recommended further detailed work, since these estimates were of a very preliminary nature.

The DOE, which defended the lawsuit on behalf of the contractor, NLO, settled the suit for $78 million in mid-1989, but admitted no wrong-doing, or even any technical problems in its own or its contractors' work. (Under the terms of its contract with the government, NLO was immune from all liability, including that arising from negligence or violations of regulations.)

But the Centers for Disease Control and Prevention (CDC) initiated an independent study of the radiation doses to the public arising from Fernald's operation.4 The final draft report of that $4 million study, prepared by Radiological Assessments Corporation (RAC), was released in August 1996.5 It corroborated IEER's critique of the official estimates of uranium releases to the air and greatly narrowed the range, estimating it to be 590,000 to 790,000 pounds, with a best estimate of 680,000 pounds.

The following table summarizes the various estimates for uranium releases from Fernald. Only the best estimate, or middle estimate, made the by source is shown:

Summary of Estimates of Uranium Releases

Institution Uranium releases to the air, pounds Uranium releases to surface water, pounds
NLO, early 1985
200,000
160,000
Westinghouse 1987
300,000
160,000
Westinghouse, 1989
400,000
160,000
IEER 1989
900,000
not made
RAC 1993
1,000,000
180,000
RAC 1996
680,000
180,000
Sources: For discussion of all release estimates and detailed references, except RAC 1993 and RAC 1996, see Makhijani 1988 and Makhijani and Franke 1989. Note that RAC published draft estimates in 1993, which it revised in 1995 and again (slightly) in 1996.
Note: Figures are rounded to one or two significant digits, as indicated.

Radon releases

The RAC study also estimated releases of other radioactive materials. The most important was radon-222 releases from the K-65 silos used for storing high radium-content waste from Belgian Congo ores. The radium-226 in the silos decayed into radon gas (as it continues to do). The deteriorating structures and poor storage conditions and practices (which were partly rectified in 1979 and then again in the 1990s) led to huge radon releases from the silos, notably in the period up to 1979. There were a few environmental measurements of radon made in 1979. IEER's preliminary work, which was focused on uranium releases and plant compliance with regulations, missed this significant source term. RAC's estimate of the radon source term for the period up to 1979 is several thousand curies per year. The cumulative radon source term estimate is 170,000 curies for the 1951-1988 period.

Radiation doses

While official DOE and contractor reports claimed that no harm had been done and that exposures to the neighbors of the plant were well under allowable limits, IEER's work found that hypothetical maximally exposed individuals near the site boundary were likely to have been exposed above allowable limits, especially during accidents. Because IEER lacked the documents regarding pollution control efficiencies, particle sizes, and chemical composition of the pollutants, as well as other factors, a reliable detailed evaluation of population risk could not be made. Moreover, the main goal of IEER's work was compliance assessment rather than population risk assessment.

In August 1996, the Radiological Assessments Corporation made public its estimates of exposures to various hypothetical individuals in scenarios designed to typify living and working patterns of people in the area. The findings were that radon exposures due to huge releases of radon gas from the K-65 silos were the main source of increased radiation risk to the population, especially for people who lived there prior to 1980. It is noteworthy that radon was not even evaluated as a source of pollution caused by the Fernald plant until the series of RAC studies in the 1990s. Radon probably also caused significant exposures to workers at the plant, a matter that remains to be addressed (see accompanying article on workers).

Doses due to uranium exposure by inhalation were the next most important factor, with other radioactive materials and pathways being judged relatively low. The table, "Comparison of Cumulative Effective Dose Contributions from Uranium Exposure Mode and Radon Decay Products" in the centerfold shows the exposures for various scenarios as calculated by RAC. The increased risk of cancer ( especially lung cancer ( are substantial in all cases. In many cases, they are comparable to the risks from smoking.

Concluding observations

The history of studies of exposure to Fernald's neighbors show that the reassurances of the DOE and its contractors -- that the nuclear weapons plants were operated safely and in compliance with applicable health and safety laws and regulations -- should not be taken at face value. The work of IEER, RAC, and others at other nuclear weapons plants indicates that DOE and contractor estimates of releases of radioactive materials are generally underestimates, and are riddled with faulty data, poor science, and calculational mistakes and inaccuracies.

Despite the settling of the lawsuit against the contractor of Fernald for $78 million of taxpayer money, concerns remain. Many studies have repudiated DOE and contractor work, showing elementary scientific flaws in it, but neither the DOE nor any of its contractors have discussed what went wrong, much less how the recurrence of scientifically dubious and misleading studies might be prevented. Many issues, such as the exposure of residents to non-radioactive pollutants and non-compliance of the plant with environmental regulations, remain unaddressed.

The DOE needs to put its own work and that of its contractors in the perspective of the findings of the independent Fernald studies. That should be the first in a series of steps that it must take to create a system that would do environmental science with at least the same vigor that DOE and its contractors addressed bomb-making.


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Institute for Energy and Environmental Research
Comments to: Outreach Coordinator: ieer@ieer.org
Takoma Park, Maryland, USA

Posted March 1997
Corrected September 2000


ENDNOTES
1. For details see Arjun Makhijani, Release Estimates of Radioactive and Non-Radioactive Materials to the Environment by the Feed Materials Production Center 1951-85, (Takoma Park: Institute for Energy and Environmental Research, 1988); and Arjun Makhijani and Bernd Franke, Addendum to the Report 'Release Estimates of Radioactive and Non-Radioactive Materials to the Environment by the Feed Materials Production Center 1951-85,' (Takoma Park: Institute for Energy and Environmental Research, 1989).

2. R.H. Starkey, memorandum to A. Meredith, "Estimated Stack Losses for December [1955]", National Lead of Ohio, 10 January 1956.

3. K.N. Ross to J.E. Beckelheimer, "Thorium Metal Production Housekeeping," National Lead of Ohio, 8 June 1970.

4. Unfortunately, the CDC did not ask for an evaluation of exposures to non-radioactive materials in its request for proposals.

5. RAC prepared a number of draft and final reports leading up to the draft 1996 report. The ones most relevant to this article are: Voillequé et al., Fernald Dosimetry Reconstruction Project: Tasks 2 and 3: Radionuclide Source Terms and Uncertainties, Draft Report (Neeses, South Carolina: Radiological Assessments Coporation, 1993); and Killough et al., Fernald Dosimetry Reconstruction Project: Task 6: Radiation Doses and Risks to Residents from FMPC Operations from 1951-1988, Draft Report (Neeses, South Carolina: Radiological Assessments Coporation, 1996).